1. The Science and Law of Air Quality Fundamental problem: Science is inexact, with a continuum of limits, errors and uncertainties –Environmental science is more uncertain than many other disciplines because it addresses biological problems in both natural and human modified situations, including human health Law tends to require a bright line demarcation between good and bad, legal and illegal. –Environmental law is all the more demanding because questions of risk and safety, cost and benefit, life and death are addressed

2. The Science and Law of Air Quality Air Quality –Science of air quality gasses Particles Risk and Safety Historical impacts of air pollution European and eastern US concerns California problems - Example: Lead and CA freeways Clean Air Act – 6 (7) criteria pollutant CO (HC), SO 2, NO 2,, ozone, lead, and TSP mass –Amendments and key modified regulations 1977 (visibility in Class 1 areas), Example: Grand Canyon 1987 TSP to PM 10 1991 (regional haze and eastern sulfur reduction), 1997 PM 10 to PM 2.5 (fine particles) Example: vf/uf, diesel, WTC

3. Global Perspective Despite using 1/5 of the worlds energy and about 1/3 of the worlds VMT, the US has much better air quality than most of the developed or developing countries Air quality in major international cities outside of Western Europe is usually appalling! California leads the nation in cleaning up smog In 1965, Los Angeles was worse than Mexico City in 1995 The Central Valley lags but still is not bad by global standards There is no way that Fresno is really the 4 th most polluted urbanized area in the US (Sacramento is listed the 7 th ) since most forms of pollution are not considered in the ranking. Blue skies and good visibility in the Sacramento Valley each Fall (rice stubble burning suppressed); Bakersfield (oil improvement)

4. Health Impacts of Air Pollution 1890 – onward - Industrial Impacts – black lung, brown lung, silicosis, toxics, ….. 1930s - Meuse Valley (FR) and Donamora, PA – 100s of excess deaths –Essentially ignored – The Great Depression London killer smog of 1952 –First serious studies; doubled death rate Los Angeles becomes a national joke – – stinging eyes, brown haze

5. Health Impacts of Air Pollution 1970s – onward – Major work of health effects of ozone in California –Health and welfare, including crops and forests 1980s – major EPA epidemiological studies – Harvard 6 cities study over 10 years; Utah valley, others –Soon becomes the Gold Standard; –introduction of PM 2.5 fine particle standard 1997 1990s – major international efforts at long term epi studies aided greatly by the decline in cigarette smoking 1990s - some gaseous pollutants de-emphasized 2000 – better animal models, etc, isolate the heart as the target of fine particles –Very fine/ultra fine particles arise as causal factors

9. Welfare Impacts of Air Pollution 1970s – onward – Major work in California –Bimodal particle size distribution and visibility reduction –Effects of gaseous pollutants (ozone, PAN) on vegetation 1977 – National visibility studies (viz CAA 1977) –Airport visibility nationwide –First aerosol measurements Class 1 areas 1980s – start of national effort at aerosols and visibility (NPS, 1981; IMPROVE 1987) –First actions under CAA 1977 plume blight – control of haze at Grand Canyon NP 1991 Kuwaiti oil fires rekindle global climate /aerosol connection –Major international studies ongoing –Aerosols now 80% of the uncertainty in global climate forcing models

10. Calculation of Risk NRC Redbook 1983 1.Hazard identification a.Qualitative evaluation of adverse effects 2.Exposure assessment a.Maximally exposed individual MEI versus b.Population at large 3.Dose response a.Animal models, scaled b.Linear extrapolation to zero 4.Risk characterization a.Reduction of lifespan b.Tumors, leukemia cases per 100,000 people in specific regions

11. Problems with Risk Assessment Maximally exposed individual is not realistic for the person with maximum exposure Repeated use of conservative assumptions (The EPA Precautionary Principle) propagates error No assessment of the fate of the pollutant under transport Failure to validate and test assumptions Entire process often happens within the EPA – science, evaluation, assessment, and standard setting, with major political conflicts of interest

12. Factors in Safety Judgments Risk assumed voluntarilyRisk assumed x 1000!involuntarily Effect immediateEffect delayed No alternatives availableMany alternatives available Risk known with certaintyRisk not known Exposure is essentialExposure is a luxury Encountered occupationallyEncountered non- occupationally Common hazardDread hazard Affects average peopleAffects especially sensitive people Will be used as intendedLikely to be mis- used Consequences reversibleConsequences irreversible

13. Protection by Criteria and Standards Criteria and standardsExample Personal exposure standardsradiation, (air?) Ambient composition standards air, water Product design standardsseat belts, cars, gasoline Product performance standards car exhaust, flammability of clothes Work practice standardsair traffic controller hours Promotional claims standardstruth in advertising? Packaging standardsChildproof pill bottles

14. Clean Air Act 109 b.1 National primary ambient air quality standards, prescribed, under subsection (a) shall be ambient air quality standards the attainment and maintenance of which in the judgment of the Administrator, based on such criteria and allowing an adequate margin of safety, are requisite to protect the public health. Such primary standards may be revised in the same manner as promulgated. –Question: Does Requisite to protect public health mean no harm to anyone? If not, which anyones dont we protect? –Question: How does Adequate margin of safety handle pollutants in which any amount produces some harm? –Question: What should California's position be to this federal mandate?

15. TSP PM 10 PM 2.5

16. Particulate Matter in the Atmospheric – the Atmospheric Aerosol Total Suspended Particulate mass TSP –< 35 μm Inhalable Aerosols PM 10 –< 10 μm Fine Aerosols PM 2.5 –< 2.5 μm Very fine aerosols, < 0.25 μm, ultra fine aerosols, < 0.10 μm 35 to 10 μm, mostly natural –Dust, sea salt, pollen, … 10 to 2.5 μm, largely natural –Dust, sea spray, some nitrates 2.5 to 0.25 μm, mostly man made –Fine dust, nitrates, sulfates, organics, smoke 0.25 to circa 0.01 μm, almost entirely man made; –high temperature combustion, heavy organics, soot, metals c 0.25 μm2.5 μm

17. Particulate Matter in the Atmospheric – the Atmospheric Aerosol Total Suspended Particulate mass TSP –< 35 μm Inhalable Aerosols PM 10 –< 10 μm Fine Aerosols PM 2.5 –< 2.5 μm Very fine aerosols, < 0.25 μm, ultra fine aerosols, < 0.10 μm 35 to 10 μm, mostly natural –Dust, sea salt, pollen, … 10 to 2.5 μm, largely natural –Dust, sea spray, some nitrates 2.5 to 0.25 μm, mostly man made –Fine dust, nitrates, sulfates, organics, smoke 0.25 to circa 0.01 μm, almost entirely man made; –high temperature combustion, heavy organics, soot, metals

18. Making of the EPA Fine Particle Standard Those who like law or sausage should never watch either one being made CAASAC – 8 of the scientists said no new PM 2.5 annual average standard was justified Of the 13 who wanted a standard, 6 said science could not support a numerical standard Of the 7 who supported a numerical standard, the choices ranged from 15 to 30 μg/m 3 (average 22 μg/m 3 ) The EPA staff recommended a standard in the range from 20 μg/m 3 to 12.5 μg/m 3 The EPA Administrator (in a room with 11 others, none of whom were scientists) chose 15 μg/m 3

19. Fine particles – age the lung and heart Statistically, excellent connection between fine particles and health, including mortality Causally, most of fine particle mass is totally harmless even in massive doses…. EPAs current thinking: health effects caused by 1.Biological agents (fungi, bacteria, viruses, spores..) 2.Acidic aerosols 3.Fine metals such as iron in the lung 4.Insoluble very fine and ultra fine particles 5.High temperature organic matter

20. Visibility reduction is mostly caused by fine particles, < 1 m; sulfates, organics (smoke), soil, nitrates, soot, and sea salt PM 2.5 PM 10

21. Example #1: Lead and the California freeways Data on human health effects of lead cause the California ARB to pass a standard - < 2.5 μg/m 3 –These levels were thought to be violated near freeways in LA, many in low income areas Research on ozone shows ARB that radical technology was needed to correct LAs problem – the catalytic converter – on all new cars –But the catalytic converter, which makes CO into CO 2 and HC into H 2 O and CO 2, needs lead free gasoline –However, the catalytic converter also changes SO 2 from the sulfur in gasoline into sulfuric acid

22. Wind

23. Effect of roadway distance and configuration on downwind concentrations of lead 1. RoadwayDistance27 m40 m100 m160 m At gradeCalculated4.0 * 3.41.40.41 * not scaled! At gradeMeasured4.03.11.40.35 DepressedMeasured4.51.70.26 ElevatedMeasured (2 sites) 4.82.33.1(3.5) (one site) 1 - per 10,000 v/hr

24. Reduction in ozone precursors in LA roughly tracks ozone decline

25. Los Angeles 1 hr Ozone Maximum Global background

26. Los Angeles Ozone 8 hr 4 th Highest 3 yr Average Global background

27. Alameda County Ozone 8 hr 4 th Highest 3 yr Average Global background

28. Fresno Ozone 8 hr 4 th Highest 3 yr Average Global background

30. Particulate Matter in the Atmospheric – the Atmospheric Aerosol Total Suspended Particulate mass TSP –< 35 μm Inhalable Aerosols PM 10 –< 10 μm Fine Aerosols PM 2.5 –< 2.5 μm Very fine aerosols, < 0.25 μm, ultra fine aerosols, < 0.10 μm 35 to 10 μm, mostly natural –Dust, sea salt, pollen, … 10 to 2.5 μm, largely natural –Dust, sea spray, some nitrates 2.5 to 0.25 μm, mostly man made –Fine dust, nitrates, sulfates, organics, smoke 0.25 to circa 0.01 μm, almost entirely man made; –high temperature combustion, heavy organics, soot, metals

31. PM 2.5 PM 0.25 ? PM 10

36. Very fine aerosols characteristic of diesels/smoking cars

37. So what if Fresno in winter is Impacted by diesels and smoking cars ? It is important to note that the estimated health risk from diesel particulate matter is higher than the risk from all other toxic air contaminants combined…. In fact, the ARB estimates that 70 percent of the known statewide cancer risk from outdoor air toxics is attributable to diesel particulate matter. The ARB does not routinely monitor diesel particulate matter concentrations. ARB Almanac 2001, pg. 346

38. Example #2: Yosemite NP, Navajo Power Station and Grand Canyon NP CAA amendments of 1977 identified Grand Canyon NP as a Class 1 area in which visibility had to be protected (to close to natural background) from human impact If an anthropogenic plume were identified as impacting the park, NPS could request EPA for hearings on mandated mitigation Navajo Power station in Page, AZ, was a large coal fired power plant with no SO 2 controls located 18 miles from the east end of the park. The NPS wanted this cleaned up! I was in charge of the aerosol science

40. Visibility reduction is mostly caused by fine particles, < 1 m; sulfates, organics (smoke), soil, nitrates, soot, and sea salt

41. Informational Resources for this Talk San Joaquin Valley Unified Air Quality Management District –http://www.valleyair.org California Air Resources Board - Almanac of Emissions and Air Quality and http://www.arb.ca.gov/html/aqe&m.htm –Routine monitoring – ADAM http://www.arb.ca.gov/adam –Special Studies - CRAPAQS, FACES, …. US Environmental Protection Agency –Routine monitoring – AIRS data base –Special studies – Fresno Super-site, US Interagency Monitoring for Protected Visual Environments (IMPROVE) – Yosemite and Sequoia NP –Routine monitoring – http://vista.cira.colostate.edu/improve/ –Special studies – Yosemite Study, summer, 2002 Research Projects – –Universities – UC Davis http://delta.ucdavis.edu (Ill post this talk) FACES, UN Reno Desert Research Inst., CORE http://nurseweb.ucsf.edu/iha/core.htm –Non Governmental Organizations – ALASET HETF, Valley Health Study and Sacramento/I-5 Transect Study; HEI www.healtheffects.orgwww.healtheffects.org Federal resources NOAA HYSPLIT http://www.arl.noaa.gov/ready/hysplit4.html http://www.arl.noaa.gov/ready/hysplit4.html